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Cartoon courtesy of MARQUIL at EmpireWire.com

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From the Desk of Senator Tom Libous
April 27, 2010

Dear ———-,

DEC announced last week that permit applications in the Syracuse and New York City watersheds will be excluded from their environmental review process. All applications for horizontal drilling in these watersheds would need to be reviewed on a case by case basis.

You can read DEC’s full announcement by clicking here.

What does that mean to us? With Syracuse and NYC watersheds having extra protection, this could do two things:

1) Help stop some of the New York City opposition to drilling.

2) Free up DEC’s review efforts to focus on permit applications outside of those areas.

We might see safe gas drilling begin sooner than we thought.

But, we still face opposition from New York City Assembly Speaker Sheldon Silver. You can read his statement on www.SafeDrillingNow.com. We have to keep fighting.

Best wishes,

Tom

________________

Sounds familiar, doesn’t it? : Two maps, two standards, part 2

Then again, maybe he reads our blog…

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November 7, 2008

Bureau of Oil & Gas Regulation
NYSDEC Division of Mineral Resources
625 Broadway, Third Floor
Albany, NY  12233-6500
Attention:  dsGEIS Scope Comments

Dear NYSDEC regulators,
I am a small landowner who is concerned that proposed gas drilling on the two large farms adjacent to my property could contaminate my water well or deplete the aquifer that supplies my well.  I plan on selling my home in the near future and need the monetary gains as part of my retirement income. My home & property value would be rendered virtually worthless if there were no water supply.  I have read the dsGEIS and feel the following items need more emphasis/study or inclusion:

Procurement of professionally trained Gas Drilling Inspectors
Requiring Gas Drilling Companies to prepare Plans and Specifications for submittal to DEC
DEC needs to thoroughly research current gas well casing cement compositions and procedures
DEC should require a gas drilling company to furnish proof of adequate liability insurance

Issue 1:  The need for PROFESSIONALLY TRAINED INSPECTORS
I worked for NYSDOT for 8yrs in the Bridge Design Unit and ODOT (Oregon DOT) for 16 yrs as a Construction Inspector and Materials Tester and later on advanced to an Associate Transportation Engineer as a Roadway Designer.  I will tell you from first hand experience that a project as simple as State Highway Asphalt Paving required an ON-SITE-DAILY- OREGON  D.O.T. TRAINED FIELD INSPECTOR and an ON-SITE-DAILY ODOT ASPHALT MATERIALS INSPECTOR testing the asphalt for such things as moisture content, percentage of asphalt in the mix, aggregate gradation sieve analysis and density.  I know this because I was this Asphalt Materials Inspector.  Thus, an operation the magnitude of the Gas Drilling Operations certainly demands the same attention!!  I stated this at the DEC meeting held in Greene and also the Coalition meeting held in Harpursville.  I also backed my concerns up with two letters to Judith Enck with a copies sent to Assemblyman Clifford Crouch asking both of them to make sure my concerns were carried to the governor prior to him signing the Bill.  I also sent an extremely detailed position description for a Canadian Oil & Gas Drilling Inspector in British Columbia, Canada.  The job description serves to illustrate the importance the Canadian government places on FIELD INSPECTIONS, and the degree of detail contained in the job description shows that gas drilling is not a simple process nor should it be treated as such!  I am extremely grateful to Gov. Paterson and his close advisors for realizing the critical need for Gas Drilling Inspectors and imposing a moratorium on all gas drilling until the state can provide a means of enforcing gas regulations.  But, recognizing the need for inspectors and finding the funding for these positions are two different things especially with the current economy.  Thus, if DEC can not currently fund inspector positions, the gas drilling should only advance as fast as the current DEC inspectors can monitor them!!

Issue 2:  Need for CONTRACT PLANS AND SPECIFICATIONS prepared by the Gas Drilling Companies themselves with submittal to the DEC for review and approval.
I attended a meeting at the Binghamton Public Library conducted by The Independent Oil & Gas Association.  I expressed the need for contract plans/specs and John Holko insisted that the Gas Drillers already provide such plans to the DEC.  The next day, I called Linda Collart of the DEC and conveyed what Mr. Holko had said.  The only thing she knew of that would be a detailed drawing of any sort consisted of ONE SHEET!  I asked her to send me a copy of one of these sheets for a recent DEC approved gas well.  This sheet shows the geological strata, depths, hole & casing design, etc.  But, this one sheet is a far-far-cry from what I am referring to and accustomed to seeing on a Dept. of Transportation project.

During my tenure with NYSDOT and ODOT, I was involved in preparing Preliminary Bridge Plans and specs for interstate bridges on 110 miles of I-88.  I also prepared Preliminary Plans for many Oregon Highway Construction projects from projects as simple as asphalt resurfacing projects all the way up to a modernization project involving widening a two lane highway to four lanes and the creation of a new alignment to meet 70mph design speeds which would avoid impacting 100yr old oak trees, four historic homes, a high power transmission line, and wetland areas.  These plans were extensive in nature, covering every known aspect of the construction and typically entailing 50 or more contract sheets with accompanying specifications of 100 or more sheets.  Thus, I don’t see a Gas Drilling Project as requiring anything less since the impacts can be every bit as far reaching.

To further drive this point home I will explain a project that I have first hand knowledge of  that was in the hands of our very own New York State DEC for review.  These were Contract Plans (24” x 36” size) drawn up by Keystone Engineers for a large pond my neighbor, located on the hill directly above me, was proposing to build.  I became very concerned with the location of this proposed pond and the fact that no one was going to be on site as an inspector to ensure adherence to the specifications.  Thus, I was successful in having DEC deny the permit for this pond.  But the main reason I bring this up is to illustrate that the division of DEC requires rather extensive PLANS and SPECS for a pond when it reaches a certain size and volume.  And I might add that a pond does not pose any risk to underground water tables nor does it contain any toxic chemicals to pollute water supplies!!  Thus, why isn’t this requirement for plans and specs carried over to the Gas Drilling Operations??  The Plans and Specs would succeed in one huge accomplishment, that being —  there would be no mystery and no doubt about what the Gas Companies might be up to; their procedures would have to be clearly explained with accompanying detailed drawings and construction notes showing every aspect of their operation.  It would be very refreshing and assuring for landowners and DEC personnel to know exactly what the Gas Drilling Plan is.

You might be thinking, what is there about a Gas Drilling Operation that would require a detailed drawing plan with accompanying specifications? ….. I will give you just one example:  Environmentalist Bob Williams gave a presentation at the Coalition meeting in Harpursville wherein he showed a picture of a gas drilling pad.  The pad was quite large and required that the earth be leveled with a berm constructed around the perimeter.  This picture caused me to immediately think of my neighbors Pond Plans and Specs.  The gas drilling berm is very much like the pond berm.  The pond berm specs state that “the embankment is to be constructed in maximum 8” thick layers running continuous for the entire length of the fill with each layer being compacted prior to placement of the next layer, and the fill is to have at least 30% passing the #200 sieve.”  Now, do you actually think the drilling pad berm was constructed in this manner??  I would bet the drill pad berm was constructed by a dozer pushin’ dirt up into an unkempt pile that was never even compacted.  Now, what was the pond berm serving to contain?  Yep, pure water.  Now what is the drill pad berm supposed to contain?  You got it, impure hazardous materials!!  As you already know, the Gas Companies are not required to disclose these hazardous materials.  However, Colorado Environmentalist Theo Colburn, PhD has discovered over 200 chemicals directly injected into the gas well during the fracturing process yet she (and I quote) “had been unable to find any information on the chemical content of waste pits until we were sent results of a chemical analysis of the residues from six waste pits in New Mexico.  The 51 chemicals that were detected in those pits produced a health pattern even more toxic than anything we found in the past.  Most important is that 43 of the 51 chemicals detected in the pits were not even on our original list of chemicals used during natural gas operations!”  Thus, this drill pad and waste pits need the same careful plan drawings and specifications as DEC requires for a fairly innocuous pond berm!!  And this is just one example of drilling details that need to be spelled out in a drawing with construction notes/specs. I know you are thinking how requiring the gas companies to develop and submit plans would slow up the gas drilling process even more than the procurement of inspectors, but this could be a good thing.  It could give the state more time to ascertain how it will obtain funding for inspector type staff.  And most of the onus of time and money to develop the plans would be placed on the Gas Drilling Companies with our DEC merely reviewing the plans which takes far less time than developing the plans.

Issue 3:  DEC needs to RESEARCH GAS WELL CEMENT COMPOSITIONS AND CEMENTING PROCEDURES and HIRE AN OUTSIDE PROFESSIONAL IN THIS FIELD SUCH AS “SCHLUMBERGER” TO REVIEW GAS DRILLING APPLICATIONS SUBMITTED TO DEC FOR APPROVAL since this is such a complicated and critical aspect of gas drilling.

In the above mentioned example of a current DEC approved gas well that Linda Collart sent me, I noticed that Class A cement was being used.  I called her to ask if this was regular Portland Cement and she said yes.  Since I used to be an Asphalt and Concrete Materials Tester for Oregon DOT, I became concerned over the rigidity of Portland Cement and the extreme conditions deep gas well bore holes and drilling operations would exert on this concrete after the casing was cemented.  Thus, I researched this topic and present the following findings:

Proper cementing is critical for the protection of subsurface aquifers and the prevention of gas leaking into zones that would otherwise not be gas bearing.  Tubing and casing leaks, poor drilling and displacement practices, improper cement selection and design, and production cycling may all be factors in the development of gas leaks.  Thus, the primary Gas drilling contractor frequently subcontracts this aspect of gas drilling to a company that exclusively performs this cementing operation. DEC personnel may have heard of “Schlumberger” since they are internationally renowned experts in this field.  I contacted them for help via email and they responded by saying “IF the DEC is interested in soliciting our help we would be willing to participate.”  (I have enclosed a copy of this email.)  Here are some of my findings on this complicated aspect of drilling that even the professionals in the Oil & Gas Industry admit that they are still in the process of perfecting.  Schlumberger says “much work remains to be done in simulating downhole conditions and developing new cement technologies/compositions for thermal applications and high pressure conditions.”

“During the life of a well, the cement sheath may be exposed to stresses imposed by well operations including perforating, hydraulic fracturing, high temperature-pressure differentials, and so on.  Further, if the well is completed using complex completion such as a multilateral system, the cement sheath may be subject to shattering and subsequent loss of bond to pipe impact.  Conventional well cement compositions are typically brittle when cured.  These conventional cement compositions often fail due to stresses, such as radial and/or tangential stresses, that are exerted on the set cement.  In other cases, cements placed in wellbores may be subjected to mechanical stress induced by vibrations resulting from operations, for example, in which wireline and pipe conveyed assembly are moved within the wellbore.  Hydraulic, thermal and mechanical stresses may be induced from forces and changes in forces existing outside the cement sheath surrounding a pipe string.  For example, overburden and geological formation pressures, formation temperatures, formation shifting, formation compaction, etc. may cause stress on cement within the wellbore.  Conventional wellbore cements typically react to excessive stress by failing.”

Halliburton offers the following:  “Wellbores exist in extremely dynamic environments; therefore, a cement sheath must be able to perform as intended over time. When cementing a well, the primary concern is to prevent fluids from migrating into an annulus.  As a well ages, the annular seal may be compromised as a result of stresses brought on by temperature and pressure cycling that occur as the well is operated.  By industry convention and tradition the effect of stresses on the cement sheath’s mechanical properties are not ordinarily assessed during the design and construction phase of a well.  Although short term considerations are necessary for effective slurry mixing and placement, a sole focus on liquid cement slurry properties and the 24 hour compressive strength does not account for long-term cement integrity, which is critical if the well is subjected to stress on a large scale.”  Halliburton has devised an analytical tool, “Welllife” computer software which analyzes properties such as Young’s modulus, friction angle, cohesion of cement sheath and simulates failure events that could occur during various field operations to determine the best cements for particular geological stratum.

Schlumberger says “cement sheath damage or debonding can allow gas to migrate to the surface and cause sustained casing pressure (SCP).  The presence of such flows can require a well to be shut in for remediation or abandoned altogether.”  Schlumberger has designed a “FUTUR active set-cement” which provides long-term zonal isolation and prevents the flow of hydrocarbons through potential leak paths up and along the annulus.  Any hydrocarbon that comes in contact with FUTUR active cement technology will activate the self-healing properties of this unique sealant material.  Once activated, cracks in the cement sheath are healed.  Even if the cement sheath is damaged again, FUTUR active set-cement will continue to self-repair on multiple, independent occasions.

Schlumberger also mentions how important it is to have a clean wellbore prior to cementing.  “It is important to get the initial cementing job right, with good mud removal.  Mud pockets in the annulus can cause catastrophic failure, including broken wellbores and collapsed casing.  Shlumberger uses WELLCLEAN methodology to ensure that there are no channels or pockets of mud that can cause well failure.  Soft formations offer little constraining pressure, and tensile pressures may lead to breakage.  Cements with a low Young’s modulus, such as the flexible cement system using FlexSTONE technology, can deliver mechanical properties appropriate for these downhole stress environments.

The following are excerpts from a paper titled “From Mud to Cement-Building Gas Wells” dated Autumn 2003 by Tom Griffin of Griffin Cementing Consulting LLC, Joseph R. Levine of the US Minerals Management Service, Dominic Murphy of BHP Billiton Petroleum to name but a few of the authors.  This study serves to illustrate the complexity of the cementing process; if the experts in this field attest to the complexity of this aspect of drilling, I think NYSDEC should pay more attention to cement designs and cementing procedures.  “Since the earliest gas wells, uncontrolled migration of hydrocarbons to the surface has challenged the oil and gas industry.  Gas migration, also called annular flow, can lead to sustained casing pressure (SCP), sometimes called sustained annular pressure (SAP).”  “In the Gulf of Mexico, there are approximately 15,500 producing, shut-in and temporarily abandoned wells in the outer continental shelf area.  United States Minerals Management (MMS) data show that 6692 of these wells, or 43%, have reported SCP on at least one casing annulus.”  “By the time a well is 15 years old, there is a 50% probability that it will have measurable SCP in one or more of its casing annuli.  However, SCP may be present in wells of any age.  In Canada, SCP occurs in all types of wells-shallow gas wells in southern Alberta, heavy-oil producers in eastern Alberta and deep gas wells in the foothills of the Rocky Mountains.  Most of the pressure buildup is due to gas.” “Long-term, durable zonal isolation is key to minimizing problems associated with annular gas flow and SCP development.”  “Determining the precise source of annular flow or sustained casing pressure is often difficult, although likely causes can be divided into four primary categories: tubing and casing leaks, poor mud displacement, improper cement-slurry design, and damage to primary cement after setting.  Leaks can result from poor thread connection, corrosion, thermal stress cracking or mechanical rupture of the inner string, or from a packer leak.  If the pressure from a leak causes a failure of the production casing the outcome can be catastrophic.  Leaks to the surface or underground blowouts may jeopardize personnel safety, production-platform facilities and the environment.”  “Inadequate removal of mud or spacer fluids from the borehole prior to cement placement is a major contributing factor to poor zonal isolation and gas migration.” “Improper cement-slurry designs –Flow occurring before cement has set is a result of loss in hydrostatic pressure to the point that the well is no longer overbalanced – hydrostatic pressure is less than formation pressure.  This decrease in hydrostatic pressure results from several phenomena that occur as part of the cement-setting process.  The change from a highly fluid, pumpable slurry to a set, rock-like material involves a gradual transition of the cement.  This may require several hours, depending on the temperature, and quantity and characteristics of retarding compounds added.  As the cement begins to gel, bonding between the cement, casing and borehole allows the slurry to become partially self-supporting.  This self-supporting condition would not be a problem if it occurred alone.  The difficulty arises because, while the cement becomes self-supporting, it loses volume as a result of at least two factors.  First, where the formation is permeable, the hydrostatic pressure overbalance drives water from the cement into the formation.  The rate of water loss depends on the pressure differential, formation permeability, and fluid loss characteristics of the cement.  A second cause pf volume loss is hydration volume reduction as the cement sets.  This occurs because set cement is denser and occupies less volume than liquid slurry.  Volume loss coupled with the interaction between partially set cement, borehole wall and casing cause a loss of hydrostatic pressure, leading to an underbalanced condition.  While the hydrostatic pressure in the partially set cement is below formation pressure, gas may invade.  If unchecked, the invasion of gas may create a channel through which gas can flow, effectively compromising cement quality and zonal isolation.  Also, cement damage can occur long after the well construction process.  Even a flawless primary cement job can be damaged by rig operations or well activities occurring after the cement has set.  Changing stresses in the wellbore may cause microannuli, stress cracks, or both, leading to SCP.  The mechanical properties of the casing and the cement vary significantly.  Consequently they do not behave in a uniform manner when exposed to changes in temperature and pressure.  As the casing and cement expand and contract, the bond between the cement sheath and casing may fail, causing microannulus, or flow path, to develop.

As the borehole reaches deeper into the earth, previously isolated layers of formation are exposed to one another, with the borehole as the conductive path.  Isolating these layers, or establishing zonal isolation, is key to minimizing the migration of formation fluids between zones or to the surface where SCP would develop.  Crucial to this process are borehole condition, effective mud removal, and cement-system design for placement, durability and adaptability to the well life cycle.  Wellbore condition depends on many factors, including rock type, formation pressures, local stresses, the type of mud used and drilling operation parameters, such as hydraulics, penetration rate, hole cleaning and fluid density balance.  The ultimate condition of the borehole is often determined early in the drilling process as drilling mud interacts with newly exposed formation.  If mismatched, the interaction of the drilling mud with formation clays can have serious detrimental effects on borehole gauge and rugosity.  Once a well is drilled, displacement, cementing and ultimately, zonal isolation efficiency are dependent on a stable borehole with minimal rugosity and tortuosity.  Drilling fluid engineers and related technical specialists have applied various techniques to investigate rock response to drilling fluid chemistry under simulated downhole conditions.  Mud companies have created high-performance water-base muds that incorporate various polymers, glycols, silicates and amines, or combination thereof, for clay control.  Like the fluids themselves, drilling fluid hydraulics play a fundamental role in constructing a quality borehole.  Balance must be maintained between fluid density, equivalent circulating density (ECD) and borehole cleaning.  If the static or dynamic fluid density is too high, loss of circulation may occur.  Conversely, if it is too low, shales and formation fluids may flow into the borehole, or in the worst case, well control may be lost.  Improper control of density and borehole hydraulics can lead to significant borehole rugosity, poor displacement and failure to achieve isolation.  Rheological properties of drilling fluids must be optimized in such a way that the frictional pressure losses are minimized without compromising cuttings-carrying capacity.  Optimal fluid properties for achieving good borehole cleaning and low frictional pressure loss often appear to be mutually exclusive.  Detailed engineering analysis is required to obtain an acceptable compromise that allows both objectives to be satisfied.  During drilling, optimal fluid characteristics may change depending on the task, such as running casing or displacement borehole fluids.  Modeling and simulation with software tools such as the M-I Virtual Hydraulics application can be useful in optimizing fluid properties in anticipation of changes in rig operations.  Integrating carefully designed drilling fluids with other key services is critical for achieving successful wellbore construction, zonal isolation and well integrity.

Proper mud selection and careful management of drilling practices generally produce a quality borehole that is near-gauge, stable and with minimal areas of rugosity, or washout.  To establish zonal isolation with cement, the drilling fluid must first be effectively removed from the borehole.  Mud removal depends on many interdependent factors.  Tubular geometry, downhole conditions, borehole characteristics, fluid rheology, displacement design, and hole geometry play major roles in successful mud removal.  Optimal fluid displacement requires a clear understanding of each variable as well as inherent interdependencies among variables.  The availability of computer technology has significantly advanced the way drillers approach wellbore displacement.  Fluids can be built, complex interactions predicted, and displacements simulated on the computer screen rather than at the wellsite where minor mistakes may result in major costs.  CemCADE cementing design and simulation software and WELLCLEAN II software are two software applications used for this purpose.

Integration of drilling fluids, spacer design and displacement techniques provide the foundation for optimal cement placement.  Long-term zonal isolation and control of gas require the cement to be properly placed and to provide low permeability, mechanical durability and adaptability to changing wellbore conditions.  Cement permeability depends on the solid fraction of the formulation.  For high-density slurries, a high solid fraction is inherent, thus the permeability tends to be low.  For low-density slurries, special products and techniques create low-density, high solid-fraction slurries.  Mechanical durability varies with strength, Young’s modulus of elasticity and Poisson’s ratio.  The cement should be designed so these properties are sufficient to prevent failure of the cement when exposed to changing well pressures and temperature fluctuations, which create stresses across the casing-cement-formation system.  Special materials are required to give the cement flexibility in this environment.    Sealing an annular space against gas migration can be more difficult in gas wells than in oil wells.  Wellbore construction, particularly in the presence of gas bearing formations, requires that borehole, drilling fluid, spacer and cement designs, and displacement techniques be dealt with as a series of interdependent systems, each playing an equally important role.  Often, the relationships among these systems is overlooked, or at the very least, poorly appreciated.  Preventing gas migration and SCP has been helped by recent developments in cementing technology that offer significant advantages in durability and adaptation to changing wellbore conditions.  Cement properties have traditionally been designed for optimal placement and strength development rather than long-term post-setting performance.  The rapid development of high cement-compressive strength after placement was generally considered adequate for most wellbore conditions.  Today, operators and service companies realize that the emphasis on strength at the expense of durability has often led to the development of SCP (sustained casing pressure) and reduced well productivity.  Cement particle characteristics and size distribution can contribute significantly to both the resistance to gas influx and maintenance of a sustainable hydraulic seal, particularly in wellbores subjected to pressure and temperature cycling.  FlexSTONE advanced flexible cement technology, part of the CemCRETE concrete-based oilwell cementing technology, is one of several solutions that effectively address cement flexibility and durability.  Conventional Portland cements are known to shrink during setting.  In contrast, FlexSTONE slurries can be designed to expand, further tightening the hydraulic seal and helping to compensate for variations in borehole or casing conditions.  This capability helps avoid microannuli development.  By adjusting specific additive characteristics and by blending the cement slurry with an engineered particle size distribution, a lowering of Young’s modulus of elasticity in cement can be achieved.  Annular cement can then flex in unison with the casing rather than failing from tensile stresses.  Thus, the potential development of microannuli and gas communication to the surface or to zones of lower pressure are minimized.”  The original complete version of the above paper can be found at  www.slb.com/media/services/resources/
oilfieldreview/ors03.

Issue 4:   DEC should not provide a well license to a person who does not furnish proof that the person has liability insurance of at least $5,000,000 per occurrence that provides compensation for all damages caused by drilling, pipeline construction, production, servicing or abandonment operations or caused by any vessel, craft or barge used to transport people or materials to the site of the drilling, pipeline construction or production operations.

I sincerely thank NYSDEC for welcoming the public’s comments on the dsGEIS and look forward to DEC’s response to my comments,

Jilda Rush

Attach:  email from Schlumberger dated 10/26/2008
British Columbia, Canada OGC Oil and Gas Commission Position Description

Cc: Gov. David Paterson, Top Advisor Judith Enck & Assemblyman Clifford Crouch

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MB writes:

I just attempted to call Grannis about this decision to do separate
reviews for NYC and Syracuse. I told the operator what my call was
about and I was transferred to the Division of Mineral Resources. I
asked them to please transfer me back to Grannis’s office. After I was
on hold for several minutes, someone answered my call and when I
explained that I was calling to register my displeasure at the plan to
give unequal treatment to different parts of the state, I was told
that they are not taking calls on this matter except through the
Division of Mineral Resources. She said that I could email my concerns
to Grannis, and then they would be documented. I told her I knew the
decision was not hers and I was not angry with her, but that I was
furious that the commissioner’s office is not taking calls on this
matter. I went ahead and told her that I was opposed to the unequal
treatment–she said she was keeping no record of the call. I told her
that I understood that, but I was telling her my position so that if
she got many, many similar calls, she could go and tell her superiors
that she had gotten a lot of calls in opposition to the unequal
treatment, even if the individual calls were not recorded. I also told
her that I have lived in and paid taxes in NY for over 25 years, and
that I bet if Chesapeake were to call about something they would get
through.

People calling about Walter Hang’s effort to get the dSGEIS withdrawn
have been getting similar treatment.

We live in this state and they are not taking our calls! Are they
deliberately trying to piss us off or what? Do they think this will
make us LESS determined to stop this nightmare? If I sound furious,
that’s because I am.

If you have not already done so, please consider calling and sending
emails to the appropriate officials to express your displeasure at the
DEC’s recent decision to create separate regulations for the NYC and
Syracuse watersheds. Phone numbers and email addresses are:

DEC Commissioner Alexander “Pete” Grannis:
518-402-8545
pgrannis@gw.dec.state.ny.us

EPA Region 2 Administrator Judith Enck:
212-637-5000
enck.judith@epa.gov

Governor David Paterson
518-474-8390
governor@chamber.state.ny.us

When contacting Grannis and Paterson, you may also wish to complain
about the fact that, as of last Friday, Grannis’s office was NOT
accepting phone calls on this issue: they were instead transferring
the calls to our “friends” over in the Division of Mineral Resources.

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Last week, high-profile news stories indicated that “DEC won’t allow gas drilling in ‘the watershed.’”  Is that true?

You may have heard or read that the NYS Department of Environmental Conservation (DEC) has decided not to allow gas drilling within the Catskill and Delaware watersheds, which supply water to NYC.

Don’t believe it.

On April 23rd the DEC announced that it will exclude unfiltered water supplies from its generic environmental impact statement. Instead gas drilling applicants will have to go through their own environmental review process to obtain permits. [1] In the 1992 GEIS there are other situations which trigger an additional environmental review.

The main question is why did the DEC decide to release this statement now, instead of including it in the final Supplemental Generic Environmental Impact Statement (SGEIS)?

Here are three good reasons for this public relations stunt:

1. To diminish public opposition

Late last October, just before the start of the public review of the draft SGEIS, Aubrey K. McClendon, the head of Chesapeake Energy, announced that his company would not drill in the Catskill and Delaware watersheds. However, he was not willing to tear up their current leases, or sign a binding agreement never to drill there. Nor could he speak for the dozens of other gas drilling companies. The public saw through his maneuver and submitted over 14,000 comments to the draft.

It seems that Pete Grannis has been taking lessons from the CEO of Chesapeake Energy.

2. To try an end run around current proposed legislation

Over two dozen bills have been introduced in the NYS legislature about gas drilling. One that is gaining momentum calls for a state-wide moratorium until 120 days after the EPA finishes its report on hydrofracking. [2] Another proposed bill calls for a state-wide ban.

The last thing the DEC and the gas industry want is a multi-year moratorium. This press release is merely an attempt to stop these bills.

3. To try to avoid some legal requirements of their environmental review

NYS is in a very difficult position because no matter what they do they are going to get sued once the SGEIS is finalized. This move is an attempt to avoid some of those legal issues. However, it’s not likely to succeed since it simply creates a new legal challenge.

The point is this: gas drilling would still be allowed in unfiltered water supplies. The DEC’s decision does not block gas drilling anyplace, and it may not be legal.

[1]. DEC Press Release: DEC Announces Separate Review for Communities With “Filtration Avoidance Determinations”

[2]. Englebright bill, A10490

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Today, two maps to ponder.   Tomorrow, why.

.

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TO:
Attn: dSGEIS Comments
Bureau of Oil & Gas Regulation
NYSDEC Division of Mineral Resources
625 Broadway, Third Floor
Albany NY 12233-6500
dmnsgeis@gw.dec.state.ny.us

FROM:
Brian Brock, retired geologist
Franklin NY

DATE:
30 December 2009

RE:    CONSIDERATIONS  FOR  REVISIONS  TO  dSGEIS

Aquifer Depths, Database of BOGR states that depths to the base of aquifer is so poorly known that they need to set a default value of 850 feet.  Despite this, there in no mention of a database for the driller’s report of the depth of fresh and brine waters at each well, which could be then used to predict depths to the base of the aquifer for future well permits.

Bedding Planes and Fractures Flow of groundwater is usually controlled by these discontinuities, but there is no adequate discussion of bedding planes and fractures in Chapter 4, Geology.  Large roadcuts, quarries, railroad tunnels, and aqueduct tunnels can provide data.

County Health Departments Many have neither the expertise or resources to investigate reports of water pollution, as suggested by SGEIS.  This responsibility is an unfunded mandate.  Health departments from counties in the fairways of the black shales should provide input.

Cumulative Impact Draft SGEIS has only a few scattered and brief discussions of this.  If a boom in extraction of gas from black shales develops in NYS (as it has elsewhere), then cumulative impacts will be substantial.  Final SGEIS should have comprehensive Cumulative Impact Assessment to include: water withdrawal, waste disposal, traffic, road damage, air pollution, manpower, and community.  Current SEQRA handbook covers cumulative impact.

Disclosure of Frac Chemicals to Public While BOGR requires that companies report all chemicals used to them, there is no provision for releasing this information to the public.  These chemicals will be injected below the public’s property and might contaminate the public’s drinking water.  Without such information, the public can not monitor the purity of its drinking water.

Fairway, Extent of Alpha Environmental consultants defines “fairway” by rock properties (pages 4-14 and 4-18) without considering the setting of the rock units.  As a result, Fig. 4.7 and 4.12 show fairways of Utica and Marcellus shales extending north and east to outcroppings.  Production of economic quantities of gas require the hydrostatic/lithostatic pressure differential produced by thousands of feet of overlying rock.  As drawn, these figures give the mistaken impression that areas that are immediately south and west of shale outcroppings will have gas extraction and should be revised.

Faulting
Figure 4.13 gives the mistaken impression that the fairways for Utica and Marcellus shales are mostly free of faults — faults that could provide pathway for waters from black shales to aquifers.  True the figure is labeled “Mapped Faults …”, but the distinction between mapped faults and total faults is not discussed.   The bedrock is monotonous and poorly exposed, so probably many faults have gone unmapped.  This figure is based on a compilation over 30 years old, and could be updated with data from natural seismicity, seismic imaging, and mapping from NYC reservoir and tunnel construction.

Figure 5-1 This schematic of a well pad  is confusing at best, and much of it is wrong.  If it is of a multi-well pad in development, then it should be so labeled.  This figure should be completely redrafted.  There is too much wrong to detail here, but contact me if you want suggestions.

Flowback Disposal
Destination  Within months of the approval of the final SGEIS, wells will each begin producing hundreds of thousand or millions of gallons of flowback.  A safe way to dispose of this is required, but there appears to be none in NYS.  Draft SGEIS does not estimate the volume of flowback expected nor discuss which sites could accept this volume.
Reporting  In Appendix 6, the proposed Environmental Assessment Form does not require reporting of frac fluids that leave New York State.  Given the lack of a significant disposal option in state, most of this water may be sent out of state.

Formation Waters, Composition of Draft SGEIS provides a summary of flowback analyses but not analyses of formation waters, despite BOGR regulating gas drilling for over a century.  Without such, several key points of the SGEIS can not be finalized, including:
* How can formation waters be distinguished from flowback?
* Can formation waters be processed through POTW?
* Can formation water be safely spread on roads?

Frac Trespass
CI Hearings Currently a hearing for compulsory integration can be held after well work is completed as long as land has been leased where drilling takes place.  Presumably a frac job is designed to fracture throughout entire drilling unit.  May they frac before the whole unit is leased or integrated?
Taking Fracing is a new technology with imperfect control of the extent of resulting fractures.  How can neighbors to the drilling unit be assured that fracing will not extend under their properties, neither trespassing nor taking “their” gas?

Funding and Staffing Although this is outside the scope of SGEIS, until BOGR obtains adequate resources for enforcement, the public can have no confidence that GEIS and SGEIS are anything more than ink on paper.

ICF International Analysis. Appendix 11
Pore Flow The mathematical analysis of fluid flow through intact rock via pore space (pp. 24 – 31) is a pointless.  There is no doubt that 1000 feet of unfractured rock would provide a barrier to frac fluids over short times, but how often is this the case?
Fracture Flow Despite wasting pages on calculating pore-flow rates, ICF dismisses chances of an open flow path from fractures, faults, or well bores as “theoretically possible but extremely unlikely” (pg. 31) without attempting to quantify this risk.  The experience of NYC in drilling their aqueduct tunnels suggest that the risk could be substantial.
Reporting Fluid Flow Even if the odds of an open flow pathway “is very small” (pg. 32), given the large number of wells expected, then occurrence of open pathways is almost certain.   Therefore one of the required non-routine incidents that drillers should report (Appendix 10, Supplementary Permit Conditions, #46) should be failure to hold pressure or anomalous fluid loss during fracing.
Injection Wells ICF consultants may be correct that high-pressure fracturing for a short time (“typically less than a day per stage”, pg. 34) make it unlikely that frac fluids could immediately reach aquifers.  On the other hand, injection wells do pump waste water at high pressures for longer times.  The consultants neglect to consider long-time flow of fluids from injection wells.  Injection wells remain one of the few ways to dispose of waste water from drilling, flowback, or plugging.
Lack of Evidence The final conclusion (pg. 34): “There are no known incidents of ground water contamination due to hydraulic fracturing.” is deceptive.  Because there has been no testing of groundwater before and after fracing by either drillers or BOGR, it is more correct to say that no proof exists that groundwater remains uncontaminated due to hydraulic fracturing.  “Absence of evidence is not evidence of absence.”

Incident Response With a large enough number of wells, everything that could go wrong will go wrong: surface spills, well seeps, aquifer pollution, fires, explosions, etc.   While SGEIS requires the reporting of any non-routine incidents by drillers, there is no mention of the response required by BOGR.

Inspections
Frequency For most wells, no inspections are required during the entire life cycle of a site: site preparations, drilling, fracturing, completing, and production.  (A single inspection during surface casing is required only for the minority of wells in primary and principal aquifers.)  Considering that much of the BOGR oversight is limited to the review of paperwork self-reported by drillers, a minimum number of random and unannounced inspections is necessary to encourage honest reporting and should be required.
Surface Casing and Initial Fracing Site visits should be required for these two steps.  These two visits by Mineral Resource Specialists would also allow inspection of the general operation.  If this is beyond the current staff, it only argues for an increase in staffing.
Transparency There is no written procedure for monitoring and inspecting a well over its life cycle from site preparation to production.  Without this, the public has no way to determine if BOGR is fulfilling its responsibility to protect the environment.
Workload BOGR has stated that it has and will continue to provide sufficient oversight of each gas well.  Should there be a rush of permit request, the number of permits issued would be limited by the workload of mineral resource specialists.  Neither final GEIS nor draft SGEIS lists what the workload is for permitting and oversight of a single well.  Nor is there a limit to the number of active wells in a mineral resources specialist’s caseload.  Without such information, the public can not be assured that BOGR is providing sufficient oversight.  Without sufficient oversight, GEIS and SGEIS are only ink on paper.

Loss of Springs and Wells During the drilling of the first several hundred feet through aquifers, there is a risk of loss or fouling of neighboring water sources until the surface casing is cemented.  Special attention in inspection or reporting should be required during this period.

LPG Fracing If this water-free fracing may someday be proposed for use in NYS, will a second SGEIS be required?  Wouldn’t it make sense to include this technology in the current SGEIS?  Obtaining and disposing of millions of gallons of water for each well constrains future fracing.

Metering Currently BOGR does not require periodic recertification of gas meters at well heads, spot check reading of meters that is done by companies, or audit company records – procedures that are routine in other states.  (These deficiencies were cited in NYS Comptroller audit 2005-S-54.)  Such procedures are required to assure that landowners and state receive what are legally due them.  The much greater volumes of gas produced by horizontal wells make a true accounting all the more important.

Methane in Groundwater Draft SGEIS mentions that methane naturally occurs in groundwater.  It does not discuss that this proves that there are pathways between black shales and aquifers — although not necessarily the targeted shales.  Gas is much more buoyant and less viscous than frac fluid, and therefore it is not clear how much of these fluids would follow the same pathways and over what time.  Nevertheless the nature and implication of these pathways should be discussed.

Multiple Plays There is substantial overlap of the fairways for Marcellus and Utica shales.  A smaller area additionally includes the fairway for Herkimer tight sandstones.  (Indeed Nornew brags that it has this “triple play” in Madison and Chenango Counties.)  There is also a chance of the spotty occurrence of Trenton/BlackRiver plays   Multiple plays multiply the effects at each well pad, but the draft SGEIS ignores the effects of multiple plays of gas, particularly on cumulative impacts.

Pollution
Bonding Drillers should be bonded for the clean-up of any pollution caused by their activities.  (Currently they are bonded only for plugging well and restoring the site.)  Commonly companies will set-up a shell company for drilling each well with assets just sufficient to cover expenses.  Without bonding, should there be major pollution, the company has no reserves that could recovered for the clean-up.
Database BOGR can state that it knows of no incident of pollution from fracing in NYS.  This claim can not be confirmed because BOGR does not maintain a database of reports of pollution.  Such a database should be built.
Liability In neighboring Pennsylvania, any pollution within 1000 feet of well head is presumed to be the responsibility of the driller who must provide sufficient water and remediate the pollution to the satisfaction of DEP.  (Purity of the provided water must be independently certified.)  There is no such provision in the final GEIS or draft SGEIS.  Without it, a individual land owner could have the expense and aggravation of dragging a polluting company through the courts for years to get satisfaction, whereas the owner needs are immediate.
Risk Despite BOGR statement that there are no case of pollution of aquifers from fracing, there are numerous documented cases of pollution of aquifers from gas drilling.  To the land owner who has lost their drinking water and a much of the value of their property, the distinction between drilling and fracing is academic.  The SGEIS should more fully discuss causes of pollution during the entire drilling process and how to eliminate any causes not covered in GEIS.

Publicly-Owned Treatment Works, Appendix 21 Despite this list of 135 POTWs, there is no guarantee that a single one of these works is capable of treating of produced waters, from drilling, flow back, or plugging.  POTW do not remove the chemicals from these waters but only dilute the toxins to below legal limits.  All the toxins are dumped into the river.  Without representative analyses of produced waters, it is not possible to even know if it is safe to pass these waters through these works or what dilution is required.  Indeed the vast majority of operators are not even considering applying for permission from DEC to accept this waste.  Including this long list in the SGEIS deceptively give the impression that there are many possible sites to receive the waste waters produced.

Refrac Permits Black shales in NYS may be refraced as soon as one year after the initial frac – although five years is more typical elsewhere.  Draft SGEIS requires a permit for refracing (8.3.2), but does not specify what information will be necessary to obtain this permit.

Road Spreading of Produced Fluids Permitting for a Beneficial Use Determination for road spreading does not specify what are the acceptable concentration of pollutants.

Set Backs, Residential GEIS requires set backs of 100 feet from drill pads to residences for a single well and this is not increased in the draft SGEIS.  This is the smallest setback of any state, with most having setbacks of 200 to 600 feet.  Even if this is adequate for single vertical wells, this is inadequate for single horizontal wells, let alone pads of multiple wells, multiple plays, and refacturings.  One site could be actively drilled and fractured for three years for a single play.

Seismic Monitoring Fracing is a developing technology with an imperfect control of the extent of resulting fractures.  Without seismic monitoring during fracing, the owners of neighboring can not be assured that gas will not be withdrawn from beneath them.  At least for a trial period, this should be required for a few wells and the results reported.

Toxicity of Chemicals Draft SGEIS does not compare the toxicity of chemicals used in drilling and fracing, claiming that there is no way to measure this: “there does not seem to be a US-based metric” pg. 9-10.  However the Federal Mineral Management Service does such rating of such chemicals in its capacity of regulator of off shore drilling. Their methodology should be applied to the land-based use of such chemicals.

Trial Period Once the final SGEIS is adopted, BOGR should begin with a limited number of permits for the new horizontal drilling and high-volume hydraulic fracturing of low permeability gas shales — maybe one multi-well pad in each county.  After a formal review, the annual number of such permits could be gradually increased.

Unconventional Gas Reservoirs While they are mentioned, it would help if there was a brief discussion of the differences among coal beds, tight sandstones, and black shales and of the differences in extracting gas from them.

Water Testing
Composition While water testing is required around the drill site, what is required to be tested does not include chemicals in frac fluids.  Without these, results  will be less useful for showing contamination.  What is more, this testing is not required to be done such that the results would be admissible in a court of law, thereby giving a false sense of security to the property owner.
Location For vertical wells, testing within a circle1000 feet in diameter may be sufficient, but for horizontal wells, a corridor at least 330 feet on either side of the horizontal well bore should be included.  Without this, BOGR is assuming that fracing could never pollute aquifers and avoiding any evidence that could contradict.

The Bureau of Oil and Gas Regulation is to be commended for compiling so much information for the SGEIS, but much work remains to be done.  Indeed, so much needs to be revised in and added to the draft SGEIS that a second round of comments will be necessary before the final SGEIS is adopted.  However from my experience with the public hearings this fall at Chenango Valley High School, comments should be limited to written submissions.



Dr. Ronald E. Bishop
Cooperstown, NY

December 30, 2009

Attention:  dSGEIS Comments
Bureau of Oil and Gas Regulation
NYSDEC Division of Mineral Resources
625 Broadway, Third Floor
Albany, NY  12233-6500

To Whom It May Concern,

Please accept my comments regarding the Draft Supplemental Generic Environmental Impact Statement for the Oil, Gas and Solution Mining Regulatory Program:  Well Permit Issuance for Horizontal Drilling and High-Volume Hydraulic Fracturing to Develop the Marcellus Shale and Other Low-Permeability Reservoirs.

Section 2.2 Public Need and Benefit

I note that economic benefits data are limited to a 5-year time frame and are nearly entirely speculative.  A more appropriate time frame would be 50 or more years, including the period after which natural gas reserves (and related revenues) have been exhausted.  Refusal to estimate (or even acknowledge) the “bust” phase that follows any projected industrial “boom” constitutes a failure to thoroughly assess the overall economic impact of this industry statewide.
In this context, it is noteworthy that gas wells in the Barnett Shales, projected to produce for 30 to 50 years, have exhibited catastrophic production decline (in spite of repeated hydraulic fracturing) after 4 to 5 years of operation (1), with overall productive life spans of only 7 to 10 years.  This suggests that technologies for recovery of gas from shales are immature; therefore, widespread application of the current state of the art runs counter to NYSDEC’s mandate to efficiently exploit the state’s natural gas reserves.  A thorough assessment of public benefit (also reflected in Section 4.4.3 Potential for Gas Production and Section 5.16.3 Production Rate) must address this issue.

Section 2.4.6 History of Drilling and Hydraulic Fracturing in Water Supply Areas

The statement, “No documented instances of groundwater contamination are recorded in the NYSDEC files from previous horizontal drilling or hydraulic fracturing projects in New York.”  is scandalous.  These kinds of projects represent a tiny minority of gas wells developed in New York, and so in no way reflect NYSDEC’s history of regulating this industry.  Numerous instances of soil and groundwater contamination caused by the gas industry were recently documented by Toxics Targeting, Inc., primarily using sources available to (or maintained by) NYSDEC (2).  Equally spurious was the statement, “The reported Chautauqua County incidents, the majority of which occurred in the 1980’s…, could not be substantiated…”  Many of these incidents occurred in the period from 2000 to the present, and were substantiated not only by the Chautauqua County Department of Health, but also by the US Geological Survey.  My own poll of New York county health officials pointed to other incidents where gas drilling appeared to impact water supplies in Allegany, Chemung, Genesee and Steuben Counties (3).  In light of such evidence, this section of the SGEIS should be stricken and replaced with a realistic assessment of gas industry culpability for collateral damage.

Section 3.2.1.1 SGEIS Applicability – Definition of High-Volume Hydraulic Fracturing

This section minimizes the pervasive issue of scale which, more than any other factor, underlies the need for updated regulations.  Compared to the GEIS’ “typical” volume of 80,000 gallons of fluids used per well, the average horizontally-drilled hydraulic fracturing project will involve over 4,000,000 gallons, 50-fold greater volume than was considered in the GEIS.  I submit that this difference is not merely “significant”; it is enormous.  For example, in spite of technological advances that permit effective additive concentrations one-tenth of those employed 10 years ago, the net result is still more than a five-fold increase in tonnage per gas well.  The accompanying increased risk in transfer-related mishaps (arguably one of the greatest potential hazards of the industry) is, in my view, severely underestimated throughout the dSGEIS.  This is particularly acute where multi-well projects are under development.

Section 5.4.3 Composition of Fracturing Fluids

This section contains gravely serious deficiencies.  First, it is inappropriate for NYSDEC to accept any less than full disclosure from energy companies regarding the chemicals they intend to use in natural gas extraction projects.  Products that are not completely described should not be permitted to be used in New York.
The catalog of health concerns noted by NYSDOH for each chemical category leaves much to be desired.  Ecological impacts of the various chemicals are entirely omitted, and some important human health effects are missed as well.
For example, one of the bromine-based biocides, 22-dibromo-3-nitrilopropionamide (DBNPA) has been shown to be extremely toxic to aquatic organisms.  In fact, DBNPA is damaging or lethal to trout, bay oysters, Mysid shrimp and Daphnia magna (so-called “water fleas”) at concentrations below its chemical detection limit (4).  The dSGEIS segment on health effects from microbicides was summarized thus:  “Toxicity information is limited for several of the microbicidal chemicals.”  This level of scientific scrutiny is dangerously inadequate for an agency charged with promoting public and environmental safety.
Worse yet, some information provided in this section is misleading.  For example, acetylenic alcohols, including propargyl alcohol, are inappropriately grouped with simple alcohols and glycols.  This group is summarized in the dSGEIS thus: “Exposure to high levels of some alcohols (e.g. ethanol, methanol) affect (sic) the central nervous system.”  Consider the toxicity of propargyl alcohol (5):  this chemical (inhaled or absorbed through the skin) induces a range of ailments that include multi-organ failure.  A sensitizer, it elicits increasing responses to decreasing exposures, and symptoms can recur months or years after all exposure has ceased.  Propargyl alcohol is widely used as a corrosion inhibitor; therefore, no discussion of health effects is adequate that fails to warn potential exposure victims about this additive.
A major question is completely omitted in this section.  No one understands, and no one at NYSDEC proposes to investigate pre-existing organisms in deep rock structures, including target formations.  What archaea, bacteria and algae currently live in these strata?  What is their value to society via biological, pharmaceutical or medical research?  How are they affected by the drastic changes imposed on their ecosystems by horizontal drilling and hydraulic fracturing?  NYSDEC should inventory, protect and develop these natural resources.
Finally, after describing (albeit incompletely) probable health effects from carcinogens, endocrine disruptors, reproductive toxins, and potentially lethal compounds planned for use at rates of hundreds or thousands of pounds per project, this section ends with the statement, “As mentioned earlier, the 1992 GEIS addressed hydraulic fracturing in Chapter 9, and NYSDOH’s review did not identify any potential exposure situations associated with horizontal drilling and high-volume hydraulic fracturing that are qualitatively different from those addressed in the GEIS.”  I submit that size matters here; a massive difference in scale requires an adjustment in regulatory approach in the same sense as different care is needed for a tiger than for a house cat.
Based on the deficiencies of this section alone, I would recommend withdrawal of this draft supplement to the GEIS for oil, gas and solution mining.

Section 5.11.1.1 Subsurface Mobility of Fracturing Fluids

This section and the associated Appendix 11 register a glaringly flawed assumption:  that fracturing fluids are being pumped into dry rock formations.  Analysis of flowback fluids clearly indicate (dSGEIS Table 5-8 and Section 5.11.3.1) that rock strata including target formations are filled with salts-saturated water, i.e. brine.  The ability of deep rock formations to accommodate additional non-compressible fluids may well depend on their ability to direct them into faults, abandoned wells or other, more porous strata.  This consideration, along with accounting for repeat hydraulic fracturing, should guide a fresh attempt to model the subterranean flow of fluids introduced at high pressures for natural gas extraction processes.

Section 5.12 Flowback Water Treatment, Recycling and Reuse

This section contains some of the most optimistic operational projections in the entire dSGEIS.  Several of the modular technologies mentioned in this section are annotated, “Modular … units have been used in the Barnett Shale.”  This might be better phrased, “… have been tested in the Barnett Shale”, because none of them are in widespread use anywhere in the US.  I suggest a more realistic set of assumptions that anticipate that 10% of flowback fluids will be reused / recycled, and the rest will require transport to distant disposal sites.

Section 5.13 Waste Disposal; 5.16.6 Brine Disposal; 5.16.7 Naturally Occurring Radioactive Materials in Marcellus Production Brine

Gas well flowback fluid is currently classified as “industrial waste” under state code (Article 27, Title 9, Paragraph 371.1. (e) (2) (v)).  However, 18 of the 69 compounds (dSGEIS Tables 5-8, 5-9, 6-1 and 6-2), as well as radionuclides (dSGEIS Appendix 13) reported in flowback fluids are listed in New York as hazardous substances.  Therefore, the NYSDEC commissioner should, by his authority under Article 27, Title 9, Paragraph 371.2 (b) (2), reclassify gas well flowback fluids as hazardous waste.
Permits for high-volume gas well development projects should not be issued unless and until intrastate infrastructure designed specifically for treating their hazardous wastes is built and functioning.

Chapter 6 Potential Environmental Impacts

Conspicuously absent from mention here are the potential impacts of residual infrastructure that remains in the ground when gas extraction activities are completed.  No complete inventory, let alone hazard assessment of abandoned oil and gas wells in New York has been assembled to date, and no long-term follow-up assessments related to proposed development are suggested in this dSGEIS.  This constitutes  a major failure in operational planning.

Section 6.1.1 Water Withdrawals

Large parts of the Southern Tier of New York situated over developable shale gas deposits lie outside regions regulated by the Susquehanna River Basin Commission, the Delaware River Basin Commission or New York City’s West of Hudson Watershed.  NYSDEC makes no provision for monitoring or limiting water withdrawals in these areas.  This constitutes a major failure in operational planning.

Section 6.1.6 Waste Transport

Manifesting of gas drilling wastes (hazardous by nature if not by state law) should be required for transport by Part 364-permitted haulers.  Description of these loads as “general industrial waste” poses unacceptable risks for emergency responders to roadway incidents.

Section 6.5 Air Quality

This elegantly researched section suffers from a failure to aggregate emissions from a number (several to several hundred) of vicinal gas wells.  Such aggregation is currently being investigated in Dish, Texas (6, 7).  Preliminary results suggest that hazardous levels of benzene, ozone and other pollutants that accumulate in an intensively drilled area can measurably influence the health of people who live there.  NYSDEC scientists would do well to study these data and consider ways to develop commensurate analytical scope in New York.

Section 6.7 Centralized Flowback Water Surface Impoundments

Central impoundments for flowback fluids should not be permitted.  Along with maintenance of pit liners and connecting conduits, maintenance of headspace should be expected to be problematic.  New York has virtually no capacity for treating these fluids (dSGEIS, (Section 5.13 Waste Disposal), and facilities in Pennsylvania are maximally utilized.  With nowhere to go, flowback in New York will build to critical (and greater) mass.  If not contained in rigid containers, this fluid will overflow into surrounding properties.  This would be particularly troublesome during periods of heavy rain or snow.

Section 6.8 Naturally Occurring Radioactive Materials in the Marcellus Shale

This section appropriately mentions the frequent occurrence of radiondclides in flowback fluids, but omits any mention of state and federal regulatory incongruities that usually complicate disposal of mixed hazard (chemical and radiological) waste.  This is particularly salient in evaluating future applications by energy companies for beneficial use determinations to permit spreading of flowback fluids on roads (Appendix 12).  I recommend consideration of these complications before any such applications are accepted.

Section 6.9 Visual Impacts

Others may consider the photos of actual wellsites in New York reassuring; I do not.  Even before scale-up to an unprecedented level of intensity, this kind of development in my region of the state should be expected to exert a significant negative impact on hunting, fishing, local recreation and tourism.  Regarding mitigation measures, I submit that “hope and wait until the worst is over” is not a viable strategy.

Chapter 7 Mitigation Measures

Throughout this section, suggestions that NYSDEC personnel should have the opportunity to supervise various critical steps in the development process (eg. surface casing cementing) should be replaced with mandates that agency personnel shall be present for any such operations.  Similarly, language proposing that mitigation steps “may” or “should” be taken should be replaced with “shall be taken”.

Section 7.1.4.2 Sufficiency of As-Built Wellbore Construction; Appendices 8, 9 & 10

Existing regulations regarding the mixing and placement of concrete are incoherent.  Particularly egregious is the requirement that poured and pumped concrete should be left undisturbed in a casing until a compressive strength of 500 pounds per square inch is achieved.  The chemistry of concrete curing is minimally defined as the hydration of calcium silicate.  The rate at which this process occurs depends heavily on several factors that include temperature, water concentration, and the presence of modifying chemicals.  All these factors are in flux with any gas well project:  (1) Temperature varies from as low as 23 deg. F at the surface to as high as 150 deg. F in the target formation – and neither extreme is ideal for curing.  (2) Water and brines are ubiquitous in New York subterranean rock strata, and can either add to or subtract from water available for curing depending on the layer depth.  (3) Commonly added fluidizers and plasticizers all tend to impede curing, but their responses to varying temperatures and water concentrations are not well characterized.
Taken together, these issues make meaningful determination of the time at which concrete throughout a well casing has reached any particular compressive strength practically incalculable.  Further, shock resistance (related to channel or crack formation) is better correlated with tensile than compressive strength.  I submit that the relative success in sealing New York gas well projects to date has been the result of many lucky guesses.  This is not a basis for sound regulation.   I strongly recommend instituting a standard period of time for waiting on concrete to cure, with the specific standard to be set by rigorous investigation of the salient parameters.
A concrete bond log should be required for every surface casing.  Further, specific site conditions under which intermediate casings must be installed should be formulated.

Section 7.1.11 Protecting the Quality of New York City’s Drinking Water Supply

I take umbrage at the notion that my or any other New Yorker’s water supply is less worth protecting than that of New York City.  Even so, the NYC Department of Environmental Protection, in its final impact assessment (8), makes clear that the best of proposed regulations are anticipated to expose New York City’s drinking water supply to substantial risk of serious damage.  Since this is the case, then acceptably safe development of gas from New York’s shales is probably not possible.  My recommended response to this realization is that NYSDEC abort any attempt to update gas development regulations and institute a state-wide ban on high-intensity gas development.

Section 7.1.12 Setbacks

This section is incoherent, lacking clarity about how interacting factors (e.g. occupied dwellings, public buildings, and various water supplies) should be interpreted in terms of setback requirements.
There is no mention of setbacks from abandoned oil or gas wells; this is a major omission.

Section 7.5 Protecting Air Quality

Frankly, major industrialization of a region is incompatible with protecting air quality.  If the goal is maintenance of air quality that is characteristic of New York’s Southern Tier today, then the mitigation measures discussed (not mandated) are doomed to failure.

Section 7.11 Mitigating Road Use Impacts

NYSDEC offers practically no assistance in this endeavor.  Municipalities should receive assistance with posting and appropriate bonding of roadways, and a centralized trust fund should be established to protect private taxpayers from having to pay for roads ruined by energy corporations and their subcontractors.  This section contains no discussion of privatization of gas revenues accompanied by socialization of the risks and costs of collateral damage, let alone any mitigation of this scenario.

Section 7.12 Mitigating Community Character Impacts

This section contains no description of existing community character with which future attributes might be compared.  Major potential impacts omitted from this section include: influences of permanent industrialization, changes in the types and numbers of cottage industries now typical of New York’s Southern Tier, and influences of the “bust” phase of a boom / bust economic cycle.  I recommend that NYSDEC conduct a rigorous examination of existing community character as prelude to an expanded discussion of impacts mitigation.

Section 7.13 Mitigating Cumulative Impacts

There is no meaningful discussion of cumulative impacts in this section, let alone any attempt to describe mitigation measures.  This constitutes one of the greatest failures of operational planning in this dSGEIS.

Chapter 9 Alternative Actions

Option 9-1, Prohibition of Development, is ruled against by NYSDEC on the basis that it would violate state law, which requires development of natural resources.  I submit that, in light of the overwhelming value of resources that would be damaged or destroyed by intensive gas extraction from New York’s shales, it is the sole legal and just option.

Appendix 15 Hydraulic Fracturing – 15 Statements from Regulatory Officials

Hydraulic fracturing has, in my view, metamorphosed from a technically challenging array of methods to release trapped gases from rocks into a caricature of all that is feared about the natural gas industry.  Judged soberly, these methods elevate risk from gas extraction processes primarily by requiring the transport, handling and use of exotic chemicals which would otherwise not need to be moved, handled, or disposed of.  In comparison to these elements of risk, the actual steps involved with “fracking” are anticlimactic – though not risk-free.
Attribution of a specific accident to any single risk factor is always fraught with difficulty, even when that factor is known by the weight of evidence to be significant.  For example, the fact that one of the drivers in an auto accident was intoxicated is not de facto evidence that the drunk driver was at fault.  Still, the drunk driver bears some responsibility.
As this issue has developed publicly, I have observed energy company spokespeople caricaturizing “hydrofracturing” as that demon which is feared by the uneducated public, but which investigators can never make culpable – provided it is considered in the narrowest methodological sense and as a sole causative factor.  I am disappointed that NYSDEC has chosen to perpetuate this caricature.
This appendix demonstrates, more than anything, the extent to which a variety of public officials are willing to collude in half-truths.  While a handful of state officials who were queried acknowledged that gas extraction produces unintentional consequences, all whose responses were included here acceded to the premise – without context, of course – that, under the narrow conditions of the question posed, hydraulic fracturing has never polluted any groundwater.
NYSDEC had the opportunity in an appendix like this to perform a valuable service of education to the public, putting issues with hydraulic fracturing into proper context.  I could not be more disappointed that you chose a different path.

Respectfully,

Ron Bishop
References Cited:

1.     Arthur Berman, “Lessons from the Barnett Shale suggest caution in other shale plays”,
ASPO International Peak Oil Conference, August 10, 2009.

2.     Walter Hang, “Drilling Spills Profiles”, Toxics Targeting, Inc. 2009

3.     Ron Bishop, “Experiences with Natural Gas Extraction:  Interviews with Health Officials
in New York’s Counties”, private communication 2009.  (Attached)

4.     EPA, “Reregistration Eligibility Decision (RED) 2,2-dibromo-3-nitrilopropionamide
(DNPA)”, September 1994.

5.     BPPB Consortium, “Propargyl Alcohol U.S. EPA HPV Challenge Program Revised
Submission”, July 2003.

6.     Jack Z. Smith, “Texas expediting environmental complaints on natural gas operations in
Barnett Shale”, Fort Worth Star-Telegram, December 23, 2009.

7.     Wilma Subra, “Results of Health Survey of Current and Former DISH/Clark, Texas
Residents”, Earthworks Oil and Gas Accountability Project, December 2009.

8.     New York City Department of Environmental Protection, “Impact Assessment of Natural
Gas Production in the New York City Water Supply Watershed: Final Impact Assessment
Report”, December 22, 2009.



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Click on image for video:

Albany, NY, January 25, 2010 (see previous posts below): While approximately 500 people were inside the Convention Center (under The Egg), a group of demonstrators paused on the New York State Capitol Building’s steps — despite the rain and 40 mph gusts — demanding a “STATEWIDE BAN” on unconventional gas drilling.

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The 01/25/2010 Albany West Capitol Park Rally of over 500 people
opposed to unconventional gas drilling was moved inside, under the Egg

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DEC workers supporting 01/25 people’s protest of the DEC’s dSGEIS (door Stop Giving Extraction Industry Shelter)… The dSGEIS  concluded that cumulative effects of tens or hundreds of thousands of toxic waste production sites would not have a cumulative effect worth considering.
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Demonstrators chanting “No fracking way!” and “Statewide ban!”
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Joan Tubridy (CDOG) speaking, with Chief Oren Lyons (Onondaga Nation) by her side. Both support a statewide ban on unconventional gas drilling. Chief Lyons called upon political leaders to consider the impact of their decisions upon the next seven generations. When Tubridy finished her listing of reasons why we should have a statewide ban, those assembled at the rally loudly chanted “Statewide ban!” for a full minute.

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Activists for statewide ban on toxic waste producing gas drilling disrupt DEC dSGEIS hearing in NYC


Video here of a portion of rally for statewide ban: 

http://www.youtube.com/watch?v=v9Pab1Hlhrs

(New York City, 11/10) A burgeoning movement to counter proposals for a two-tiered standard of environmental protection from shale gas drilling in New York State erupted in the first New York City DEC hearing on the proposed State regulations. The filled-to-capacity hearing began – as usual – with elected officials testifying, with clear intent that they would leave before listening to the hours of testimony for a statewide ban by New York City residents. But as Deputy Mayor Ed Skyler introduced his divisive approach of protecting only a small portion of the State’s vast environment, a city representative of the movement for a statewide ban on the dangerous practice walked up onto the stage.

Taking the stage, Alex Johnson, a life-long resident of New York City, declared to much applause, “We want a statewide ban. We don’t need hearings to regulate this. Gas drilling is dangerous and we need to ban it. We stand with thousands of New Yorkers –and most of you here tonight– in demanding a statewide ban on the use of the destructive fossil fuel extraction process known as hydraulic fracturing in New York’s Marcellus and other shales.”

Alluding to the rally for a statewide ban and the simultaneous press conference by Manhattan Borough President Scott Stringer to ban drilling in the “New York City watershed”  Johnson emphasized, “We reject the divisive call for a ban for New York City’s water by slippery politicians and corporate environmental organizations. We call on elected officials to represent the clear opinions of experts and citizens that this process is too dangerous to allow anywhere in New York State.”

Many New Yorkers in the audience applauded and continued to speak out. Wendy Malcom of the Safe Water Movement stood up in the audience calling for recognition that the DEC hearing was merely to facilitate drilling. “Don’t Frack New York State,” Ms. Malcom chanted. “Groups across the state including the Haudenosaunee Iroquois Confederation declared they would not participate in the drilling hearing because the DEC is using the hearings to promote gas drilling. Our communities and the planet are facing a climate catastrophe that requires Governor Paterson to ban gas drilling and promote a transition to 100% renewables within 10 years.”

Fifty-one (51) organizations across New York State (many based in New York City) have declared their support of a statewide ban as expressed in the recently released petition.

Johnson shouted as he was being escorted that “the DEC is mandated to facilitate even environmentally disastrous gas exploration and drilling in our State. Governor Paterson can ban this process. The electorate must reclaim control over the commons, to protect our water supplies from irreversible contamination, and to develop sustainable energy alternatives.”


The intervention by the twenty activists was met with much applause. Some were escorted from the hearing place.

For more information, go to www.un-naturalgas.org
For interviews, call: Laura Sheinkopf, 516.314.0011

To NYC statewide drilling ban activists -
from your fellow fighters upstate,

t h a n k  y o u



DELAWARE-OTSEGO AUDUBON SOCIETY
PO Box 544, ONEONTA, NY 13820

NEWS RELEASE

FOR IMMEDIATE RELEASE: 11/2/09

AUDUDON GROUP OPPOSES HYDROFRACTURING, CALLS PROCESS AN UNACCEPTABLE DANGER

The Delaware-Otsego Audubon Society has announced its opposition to hydrofracturing gas exploration and production in our region. In a recent statement released by the group, DOAS also calls on NY State to permanently ban the practice.

Dangers to humans, wildlife, and water resources were cited as primary reasons the group finds hydrofracking unacceptable. The statement details multiple areas of concern created by injecting hundreds of millions of gallons of water treated with toxic chemicals under ground at extremely high pressures.

“After a careful review, our board of directors found it unacceptable to expose present and future generations to the contamination produced by this drilling technique,” said DOAS president Tom Salo. The group’s statement calls hydrofracking ” . . . an assault on the very resources that sustain life,” and says, “this damage will remain for millennia, and will threaten unseen future generations, as well as present-day humans and wildlife.”

Other reasons cited for the group’s opposition include wildlife and social impacts from noise and air pollution, large water withdrawals, and damage to habitats and roads from pipelines and wells.

The DOAS statement reads “Hundreds of wells are anticipated for our area, and this may change the region to a permanent industrial landscape. Potential contamination and depletion of water, and pollution of air, soil, and of farm and forest ecosystems could destroy the many resources available today. Water withdrawal and contamination are of special concern. The fragmentation and loss of habitats, and the disturbances of noise and traffic will have an adverse affect on birds and other wildlife, some already in precipitous decline.”

A recently released impact statement from the NY State Department of Environmental Conservation is insufficient to overcome the fundamental threats from hydrofracking, according to DOAS Director Jean T. Miller. “How can we engineer away permanent physical changes and poisoning of the earth?” she said. “We are trading a few more years of fossil fuels for tens of thousands of years of damaged and tainted ground below us.”

Regarding the DEC proposal, DOAS’ statement reads, “Even with the most stringent controls and oversight, this activity is an unacceptable danger to our planet, with no environmental benefits.”

The Audubon group is calling upon the state of New York to permanently ban hydrofracking. “In our view, there is no way this can be done without serious and long-term negative impacts,” said Salo. DOAS is urging the public and their members to contact DEC on the Draft Supplemental Generic Environmental Impact Statement before November 30. Comments should be sent to

dSGEIS Comments,
Bureau of Oil & Gas Regulation, NYSDEC Division of Mineral
Resources, 625 Broadway, Third Floor, Albany, NY 12233-6500,

or submitted on-line at DEC’s website.

The DOAS position on gas drilling and hydrofracking wells can be found on their website <http://www.doas.us/>www.doas.us.

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